A sulfide-carbon superlattice (MoS 2-C) is designed and fabricated as cathode for all-solid-state lithium battery (ASSLB).The alternating stacking structure of MoS 2 and carbon layers endows it with exceptional structural stability, rapid lithium-ion diffusion, and enhanced electronic conductivity. Thus, conductive additive-free ASSLB was successfully obtained,
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The inclusion of conductive carbon materials into lithium-ion batteries (LIBs) is essential for constructing an electrical network of electrodes. Considering the demand for cells in electric vehicles (e.g., higher energy density and lower cell cost), the replacement of the currently used carbon black with carbon nanotubes (CNTs) seems inevitable. This review discusses
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Results of hazard endpoint assessments for 103 electrolyte chemicals used in lithium‐ion (Li‐ion) batteries, aggregated into seven chemical groups: (A) salts, (B) carbonates,
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The increasing energy storage demand for electric vehicles and renewable energy technologies, as well as environmental regulations demanding the reutilizing of lithium-ion batteries (LIBs). The issue of depleting resources, particularly Li, is a major issue. To lessen the environmental risks brought on by the mining of metals and spent LIBs, efforts should be made in the field of
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In this paper, the retired Electric vehicles lithium-ion batteries (LIBs) was the research object, and a specific analysis of the recycling treatment and gradual use stages of power batteries were based on life cycle assessment. Different battery assessment scenarios were established according to the development of battery recycling in China.
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the environmental burden was the supply of metal material for the LFP . Many researches of the environmental impact assessments for power lithium-ion batteries were carried out early [8–11]. However, the environmental impacts analyses of cathode materials for the power batteries associated with Chinese sit-
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Conductive carbon black meets the low-cost characteristics of lithium iron phosphate batteries. The conductivity of lithium iron phosphate battery itself is worse than that of ternary battery, so more conductive agent needs to
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Currently, the large-scale implementation of advanced battery technologies is in its early stages, with most related research focusing only on material and battery performance evaluations (Sun et al., 2020) nsequently, existing life cycle assessment (LCA) studies of Ni-rich LIBs have excluded or simplified the production stage of batteries due to data limitations.
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But generally, a reliable and precise LCA study of lithium batteries highlights the need for lab-scale environmental assessments to bridge the gap between laboratory and industrial-scale evaluations, as demonstrated by studies identifying production hotspots in lithium-ion battery manufacturing (Erakca et al., 2023) and environmental comparisons between all
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Designing thick electrodes is essential for applications of lithium-ion batteries that require high energy densities. Introducing a dry electrode process that does not require solvents during electrode fabrication has gained significant attention, enabling the production of homogeneous electrodes with significantly higher areal capacity than the conventional wet electrode process.
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Review of lithium-ion batteries'' supply-chain in Europe: Material flow analysis and environmental assessment The environmental assessment of recycling reported the GHG emissions -i.e., the global warming potential, the only impact category available in all selected references. Most common leaching agent is sulfuric acid (Chan et al
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Environmental impacts regarding LiNi1/3Mn1/3Co1/3O2 cathode hydrometallurgical recycling are quantified using life-cycle assessment for a sustainable circular lithium-ion battery industry.
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Battery technology represents a complex system with numerous parameters, considerations, and dependencies, posing challenges in regulating environmental, economic, and technological aspects (Turetskyy et al., 2020).An environmental study reveals that the impact of Li-ion batteries in the production phase remains higher than that of lead-acid batteries (Fan et
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Olivine-type LiFePO 4 has attracted extensive attention owing to its low cost, high theoretical capacity (170 mAh/g), good cycle performance, excellent thermal stability, environmental friendliness, low self-discharge rate, and safety [1,2,3,4,5].However, due to its low conductivity and lithium ion diffusion coefficient, the internal resistance of the battery is high, thus affecting
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Graphene, carbon nanotubes, and carbon black conductive agents form an efficient network in lithium iron phosphate cathodes, enhancing conductivity and improving battery cycle life and performance.
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Review of lithium-ion batteries'' supply-chain in Europe: Material flow analysis and environmental assessment March 2024 Journal of Environmental Management 358:120758
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This study presents a comprehensive life cycle assessment (LCA) of calcium-based polymer electrolytes, aiming to advance sustainable solid-state post-lithium battery
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Lithium-ion batteries (LIBs) generate electrical energy through the conversion of chemical energy .Applications can range from portable devices to vehicles, i.e., electric vehicles (EVs), plug-in hybrid electric vehicles (PHEVs), to an accumulation system, i.e., an energy storage system (ESS) .LIBs provide higher energy and power densities than conventional
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Lithium, cobalt, and nickel are crucial feedstocks for lithium-ion batteries (LIBs) production, especially for ternary LIBs (Olivetti et al., 2017; Dehghani-Sanij et al., 2019; van den Brink et al., 2020; Zhang et al., 2023a).The consumption of lithium-ion battery production has reportedly surged, rising from 35% in 2015 to 80% in 2022, indicating a consistent upward
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The results showed that the use of recycled materials in battery manufacturing would reduce environmental damage (Dai et al., 2019). calculated the total energy use, greenhouse gas emissions, and water consumption of NCM batteries from “cradle to gate” and found that the energy use of cathode active materials (CAMs), aluminum, and battery
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Lithium-ion batteries with an LFP cell chemistry are experiencing strong growth in the global battery market. Consequently, a process concept has been developed to recycle and recover critical raw materials, particularly graphite and lithium. The developed process concept consists of a thermal pretreatment to remove organic solvents and binders, flotation for
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Research gaps in environmental life cycle assessments of lithium ion batteries for grid-scale stationary energy storage systems: End-of-life options and other issues
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The MOF cathode should have good wettability with the electrolyte and exhibit good rheological properties when mixed with binders and conductive agents. In 2007, Tarascon et al. first reported the use of MIL-53(Fe) as a cathode material for lithium-ion batteries.
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The future perspective of conducting LCA of batteries will likely involve addressing and overcoming several ongoing challenges. These challenges are expected to evolve as technology advances as the understanding of sustainability deepens. Life cycle environmental assessment of lithium-ion and nickel metal hydride batteries for plug-in
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The development of lithium-ion batteries with high-energy densities is substantially hampered by the graphite anode''s low theoretical capacity (372 mAh g −1). There is an urgent need to explore novel anode materials for lithium-ion batteries.
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Faculty of Environmental Science and Engineering, Kunming University of Science and Technology, Kunming, Yunnan, 650500 China. of new highly conductive carbon-based conductive agents has become a mainstream trend in the research of anode conductive agents for lithium-ion batteries. At present, the conventional conductive agent cannot meet
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The environmental impact of lithium-ion batteries (LIBs) is assessed with the help of LCA (Arshad et al. 2020). Previous studies have focussed on the environmental impact
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Life Cycle Assessment (LCA) is a systemic tool for evaluating the environmental impact related to goods and services. It includes technical surveys of all product life cycle stages, from material acquisition and manufacturing to use and end-of-life(Nordelöf et al., 2014).With regard to the battery, the LCA is one of the most effective ways of exploring the resource and
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battery choices that rely on Earth-abundant materials. 2. Experimental Section 2.1. Goal, Scope, and Life Cycle Inventory The goal of this work was to apply the cradle-to-gate LCA meth-odology to quantify and compare the environmental impacts of six representative SPEs applied into solid-state lithium batteries.
Learn More This review offers a comprehensive study of Environmental Life Cycle Assessment (E-LCA), Life Cycle Costing (LCC), Social Life Cycle Assessment (S-LCA), and
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The environmental impacts of six state‐of‐the‐art solid polymer electrolytes for solid lithium‐ion batteries are quantified using the life cycle assessment methodology.
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Abstract The use of all-solid-state lithium metal batteries (ASSLMBs) has garnered significant attention as a promising solution for advanced energy storage systems. the potential of ASSLMBs, solid-state electrolytes (SSEs) must meet several requirements. These include high ionic conductivity and Li + transference number, smooth interfacial
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Energy & Environmental Science. Dry-processed thick electrode design with a porous conductive agent enabling 20 mA h cm −2 for high-energy-density lithium-ion batteries Designing thick electrodes is essential for applications of lithium-ion batteries that require high energy densities. Introducing a dry electrode process that does not
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However, the low ionic conductivity of PEO-based SPEs at ambient temperature, poor temperature stability, and narrow electrochemical stability window hinder its application in
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To understand the environmental sustainability performance of Li-S battery on future EVs, here a novel life cycle assessment (LCA) model is developed for comprehensive environmental impact assessment of a Li-S battery pack using a graphene sulfur composite cathode and a lithium metal anode protected by a lithium-ion conductive layer, for actual EV
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By introducing the life cycle assessment method and entropy weight method to quantify environmental load, a multilevel index evaluation system was established based on
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Here, we introduce an environmentally friendly way of fabricating carbon nanoparticles which can be utilized as conductive agent for lithium-ion batteries (LIBs). Polyethylene (PE), which comprises the largest
Learn MoreBy providing a nuanced understanding of the environmental, economic, and social dimensions of lithium-based batteries, the framework guides policymakers, manufacturers, and consumers toward more informed and sustainable choices in battery production, utilization, and end-of-life management.
Life cycle assessment (LCA) of lithium-oxygen Li−O 2 battery showed that the system had a lower environmental impact compared to the conventional NMC-G battery, with a 9.5 % decrease in GHG emissions to 149 g CO 2 eq km −1 .
The lithium-ion battery pack with NMC cathode and lithium metal anode (NMC-Li) is recognized as the most environmentally friendly new LIB based on 1 kWh storage capacity, with a cycle life approaching or surpassing lithium-ion battery pack with NMC cathode and graphite anode (NMC-C).
For instance, the goal may be to evaluate the environmental, social, and economic impacts of the batteries and identify opportunities for improvement. Alternatively, the goal may include comparing the sustainability performance of various Li-based battery types or rating the sustainability of the entire battery supply chain.
Akasapu and Hehenberger, (2023) found similar conclusion that Global Warming Potential (GWP) and Abiotic Depletion Potential (ADP) are critical factor for environmental impacts . The current findings also reveal that climate change (fossil) contribute the major environmental impacts during LCA of lithium ion batteries.
The lithium-ion battery life cycle includes the following steps: 1. Mining /Extraction of raw materials used for its package and cells. 2. 3. Manufacturing of intermediate products (cathode, anode, electrolytes) that is used for the construction of pack and cells. 4. 5. 6. 7.
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